Canada Gazette, Part I, Volume 147, Number 37: GOVERNMENT NOTICES
September 14, 2013
DEPARTMENT OF THE ENVIRONMENT
MIGRATORY BIRDS CONVENTION ACT, 1994
Notice with respect to temporary possession of migratory birds
In order to conduct a survey about avian viruses, the Canadian Minister of the Environment has issued a notice under the authority of section 36 of the Migratory Birds Regulations to vary the application of paragraph 6(b) of the Migratory Bird Regulations to allow for the temporary possession of found-dead migratory birds. A person is permitted to temporarily possess dead migratory birds to allow for “swift delivery” of such birds to provincial or territorial authorities for analysis. In all other circumstances, a prohibition against possessing the carcass of a migratory bird remains in effect. This notice comes into force for a period of one year from August 28, 2013. The Government of Canada is responsible, under the Migratory Birds Convention Act, 1994, for ensuring that populations of migratory birds are maintained, protected and conserved.
The Canadian Cooperative Wildlife Health Centre coordinates Canada’s Interagency Wild Bird Influenza Survey. Information on where to submit found-dead migratory birds is available by viewing the Canadian Cooperative Wildlife Health Centre Web site at www.ccwhc.ca/contact_us.php?language=en or by telephoning 1-800-567-2033. Guidance on precautions for the handling of wild birds is available from the Public Health Agency of Canada on its Web site at www.phac-aspc.gc.ca/influenza/fs-hwb-fr-mos-eng.php.
August 28, 2013
SUE MILBURN-HOPWOOD
Director General
Canadian Wildlife Service
[37-1-o]
DEPARTMENT OF HEALTH
CANADIAN ENVIRONMENTAL PROTECTION ACT, 1999
Guideline for benzene in residential indoor air
Pursuant to subsection 55(3) of the Canadian Environmental Protection Act, 1999, the Minister of Health hereby gives notice of a qualitative guideline for benzene in residential indoor air, to be cited as “Guidance for Benzene in Residential Indoor Air.”
July 31, 2013
AMANDA JANE PREECE
Director General
Safe Environments Directorate
On behalf of the Minister of Health
ANNEX
GUIDANCE FOR BENZENE IN RESIDENTIAL INDOOR AIR
Background
Benzene is a volatile organic compound (VOC) with a relatively high vapour pressure, moderate-to-high water solubility, and low octanol/water partition coefficient that is released primarily to air. It has been identified by Health Canada as a priority indoor air contaminant through consultations with provincial and territorial health departments, as well as with key stakeholders in industrial and environmental organizations.
Exposure
Exposure of the general Canadian population to benzene is attributed predominantly to indoor air by inhalation because indoor levels generally exceed those outside, and time spent indoors is typically greater than time spent outdoors. Other routes of exposure (ingestion and dermal absorption) contribute minimally to total benzene intake (Health Canada, 2009). In studies by Health Canada, the median concentrations of benzene measured in Canadian residences range from 0.5 to 2.2 µg/m3 (Health Canada, 2012; Health Canada, 2010a; Health Canada, 2010b; Héroux et al., 2008). Indoor levels are approximately threefold higher in homes with attached garages compared to those in homes with detached garages, or no garages. Median outdoor concentrations are usually less than 1 µg/m3. The ratio of indoor/outdoor levels (I/O) ranges from 1.5 to 2.4 (median) and remains above 1 at the 25th percentile, suggesting a significant contribution of indoor sources in almost all homes.
More than half of Canadian single-family homes have an attached garage. Attached garages, when present, are the major indoor source of benzene in homes because vehicle exhaust and evaporative emissions from gas-powered equipment and stored solvents in garages can enter a home (Héroux et al., 2010; Héroux et al., 2008; Jia, Batterman and Godwin, 2008; Batterman, Jia and Hatzivasilis, 2007). Smoking is also a significant contributor to indoor benzene levels (Héroux et al., 2010; Héroux et al., 2008).
The known sources could not account for all benzene measured in studies and there may be other unidentified sources in homes. Some non-smoking homes without attached garages may have indoor benzene levels similar to those in homes with attached garages. While benzene has been detected in building materials, emission rates have generally been low (<4 µg m-2 h-1) with few exceptions (e.g. adhesives and caulking) [Choi et al., 2010; Won et al., 2005; Yu and Crump, 1998; U.S. EPA, 1992; Wallace, Pellizzari and Leaderer, 1987]. Few household or consumer products have reported benzene content (Kwon et al., 2008; Kwon et al., 2007; Sack et al., 1992; U.S. EPA, 1992; Wallace, Pellizzari and Leaderer, 1987) and, in the majority of studies, benzene was not associated with household products or activities (Missia et al., 2010; Héroux et al., 2008; Jia, Batterman and Godwin, 2008; Jia, D’Souza and Batterman, 2008; Park and Ikeda, 2006; Brown, 2002; Ilgen et al., 2001; Kim, Harrad and Harrison, 2001). Therefore, a more systematic approach to identifying other sources of benzene indoors is warranted.
Another potential indoor source of benzene would be vapour intrusion if the groundwater or soil underlying the house is contaminated. In addition, if benzene is present in the domestic water supply, volatilization from water during bathing or showering, or while water is running from faucets may occur. The Health Canada drinking water guideline has been developed to account for all exposure pathways (ingestion, inhalation, dermal absorption); thus, if a water supply complies with the drinking water guideline regarding benzene content, the health risk of such exposure would be negligible.
Health effects
Human exposure to benzene has been linked to dizziness, tremors, nausea, vomiting, headache, and drowsiness after minutes of exposure to high levels in the range of 700 to 3 000 ppm (2 240 to 9 600 mg/m3). Effects after subchronic to chronic exposures as low as <1 ppm (<3.2 mg/m3) include progressive deterioration in hematopoietic function, including bone marrow damage, changes in circulating blood cells and altered immune response (ATSDR, 2007).
Benzene is classified as a carcinogen (U.S. EPA, 1998; Environment Canada and Health and Welfare Canada, 1993; IARC, 1987). Benzene affects the blood-forming system at low levels of occupational exposure ≤1 ppm (3.2 mg/m3), and there is no evidence of a threshold. Chronic exposure to benzene has been shown to cause leukemia, a cancer of the blood or bone marrow, in occupationally exposed workers; and leukemia and lymphomas in laboratory rats and mice (Health Canada, 2009; OEHHA, 2001; Hayes et al., 1997; Rinsky, Young and Smith, 1981). The carcinogenic mode of action for benzene is not well understood; however, a series of important biological events progressing from metabolism to development of leukemia has been proposed (Meek and Klaunig, 2010).
Health Canada and other organizations have characterized the cancer risk associated with exposure to benzene in air (Health Canada, 1996; OEHHA, 2001; U.S. EPA, 2000). All of these values can be expressed as an increased risk of leukemia over a lifetime. The basis for these values is epidemiological studies of occupationally exposed individuals. The derivation of any reference value requires careful consideration of many factors and the adoption of several assumptions. Differences in these key inputs are reflected in the range of published toxicological reference values for benzene. However, considering the uncertainties identified with extrapolation of risks associated with exposures at occupational levels to lower, environmentally relevant concentrations, the shape of the dose-response curve and the mode of action of benzene-associated leukemia, these reference concentration values are within a similar band of uncertainty.
From the cancer risk analyses by Health Canada (1996), the United States Environmental Protection Agency (U.S. EPA, 2000) and the California Environmental Protection Agency’s Office of Environmental Health Hazard Assessment (OEHHA, 2001), the concentrations associated with a 1 × 10-6 (one in one million) risk of leukemia range from 0.06 µg/m3 (the most justifiable unit risk identified by the OEHHA [2001]) to 0.45 µg/m3 (the upper bound of the range presented by U.S. EPA [2000]). Guidance on benzene levels indoors has been developed by the World Health Organization (WHO, 2010) and the European Commission (2005). Both of these organizations suggest that benzene levels indoors should be minimized as much as possible, but neither organization has developed a numerical guideline value for benzene levels indoors.
The real cancer risk from benzene in most Canadian homes, while not always negligible, is uncertain. Environmental levels are at least three orders of magnitude lower (in µg/m3 range) than the occupational exposure levels in the key studies (in mg/m3 range), and conservative assumptions were used when extrapolating from the risks based on high exposures. However, the uncertainty associated with the estimation of cancer risk at environmental exposure levels may be reduced when a clear mode of action of benzene toxicity in humans is established and applied to better estimate the dose-response relationship at low exposures.
Guidance
The range of estimates of carcinogenic risks of benzene indicates that there may be a low but non-negligible risk at indoor exposure levels. On this basis, from a practical perspective, Health Canada has opted to use a qualitative approach, recommending that individuals take actions to reduce exposure to benzene indoors as much as possible. Measures to control known indoor sources may reduce benzene concentrations such that the risk to residents is very low. As further sources are identified and effective control measures developed, Health Canada will incorporate additional recommendations on reducing benzene levels in its communications to health and building professionals and the public.
While all indoor sources of benzene in Canadian homes could not be characterized, addressing the strongest predictors identified is likely to have the most significant impact on indoor levels. Exposure reduction strategies should be targeted towards the primary sources of benzene indoors over which homeowners have control, namely attached garages and indoor smoking. Indoor benzene levels may be minimized by
- Preventing leaks from an attached garage to the house;
- Making sure that there is an appropriate seal between the home and the garage, particularly for any door that connects the two. This can be achieved by providing an appropriate air barrier and a sealed door between the garage and house and drywalling shared walls between the garage and house. These actions will also reduce the air exchange between the home and the garage;
- Installing an exhaust fan in an attached garage;
- Not idling vehicles in an attached garage;
- Not starting gas-powered equipment in an attached garage; and
- Not smoking inside the home or the garage.
Where possible, removing solvents and gas-powered equipment, tools or engines from attached garages, since most small engines do not have emission controls on evaporative releases, may also be considered.
While there is some evidence (CMHC, 2004; Ilgen et al., 2001) to support a reduction in indoor benzene levels originating from attached garages following these exposure reduction strategies, further research is required to understand which mitigation measures are the most technically feasible and cost-effective at reducing the migration of benzene from attached garages indoors. As well, research is needed into the predictors of elevated benzene in homes with detached garages or without garages.
References
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ATSDR. (2007) “Toxicological Profile for Benzene.” Agency for Toxic Substances and Disease Registry, Public Health Service, U.S. Department of Health and Human Services, Atlanta, GA, 1–438. Available at www.atsdr.cdc.gov/toxprofiles/tp.asp? id=40&tid=14.
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Batterman, S., Jia, C. and Hatzivasilis, G. (2007) “Migration of volatile organic compounds from attached garages to residences: A major exposure source.” Environmental research, 104(2), 224–240.
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Brown, S. K. (2002) “Volatile organic pollutants in new and established buildings in Melbourne, Australia.” Indoor air, 12(1), 55–63.
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Choi, D. H., Kang, D. H., Kim, S. S., Yeo, M. S. and Kim, K. W. (2010) “The impact of a non-adhesive floating installation method on emissions and indoor concentrations of VOCs.” Indoor and Built Environment, 19(4), 435–443.
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CMHC. (2004) “Garage Performance Testing. Technical Series 04-108.” Research Highlight. Canada Mortgage and Housing Corporation.
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Environment Canada and Health and Welfare Canada. (1993) “Canadian Environmental Protection Act. Priority Substances List Assessment Report: Benzene.” Minister of Supply and Services Canada, Ottawa, Ontario. Available at www.hc-sc.gc.ca/ewh-semt/alt_formats/hecs-sesc/pdf/pubs/contaminants/ psl1-lsp1/benzene/benzene-eng.pdf.
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European Commission. (2005) “The INDEX Project: Critical Appraisal of the Setting and Implementation of Indoor Exposure Limits in the EU.” Joint Research Centre, 1–331.
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Hayes, R. B., Yin, S. N., Dosemeci, M., Li, G. L., Wacholder, S., Travis, L. B., Li, C. Y., Rothman, N., Hoover, R. N. and Linet, M. S. (1997) “Benzene and the dose-related incidence of hematologic neoplasms in China.” Journal of the National Cancer Institute, 89(14), 1065–1071.
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Health Canada. (2012) “Halifax Indoor Air Quality Study (2009): Volatile Organic Compounds (VOC) Data Summary.” Health Canada, Ottawa, Ontario K1A 0K9.
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Health Canada. (2010a) “Regina Indoor Air Quality Study (2007): Data Summary for Volatile Organic Compound Sampling.” Health Canada, Ottawa, Ontario K1A 0K9.
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Health Canada. (2010b) “Windsor Exposure Assessment Study (2005-2006): Data Summary for Volatile Organic Compound Sampling.” Health Canada, Ottawa, Ontario K1A 0K9.
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Health Canada. (2009) “Guidelines for Canadian Drinking Water Quality: Guideline Technical Document — Benzene.” Health Canada, Ottawa. Available at www.hc-sc.gc.ca/ ewh-semt/alt_formats/hecs-sesc/pdf/pubs/water-eau/benzene/ benzene-eng.pdf.
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Health Canada. (1996) “Health-Based Tolerable Daily Intakes/ Concentrations and Tumorigenic Doses/Concentrations for Priority Substances.” Minister of Supply and Services Canada.
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Héroux, M. È., Clark, N., Ryswyk, K. V., Mallick, R., Gilbert, N. L., Harrison, I., Rispler, K., Wang, D., Anastassopoulos, A., Guay, M., MacNeill, M. and Wheeler, A. J. (2010) “Predictors of Indoor Air Concentrations in Smoking and Non-Smoking Residences.” International Journal of Environmental Research and Public Health, 7, 3080–3099.
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Héroux, M. È., Gauvin, D., Gilbert, N. L., Guay, M., Dupuis, G., Legris, M. and Lévesque, B. (2008) “Housing characteristics and indoor concentrations of selected volatile organic compounds (VOCs) in Quebec City, Canada.” Indoor and Built Environment, 17(2), 128–137.
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IARC. (1987) “Benzene.” In: “Overall evaluations of carcinogenicity: An updating of IARC Monographs volumes 1-42.” IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Man, Supplement 7, 120.
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Ilgen, E., Levsen, K., Angerer, J., Schneider, P., Heinrich, J. and Wichmann, H.-E. (2001) “Aromatic hydrocarbons in the atmospheric environment. Part Ⅱ: Univariate and multivariate analysis and case studies of indoor concentrations.” Atmospheric Environment, 35(7), 1253–1264.
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Jia, C., Batterman, S. and Godwin, C. (2008) “VOCs in industrial, urban and suburban neighborhoods, Part 2: Factors affecting indoor and outdoor concentrations.” Atmospheric Environment, 42(9), 2101–2116.
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Jia, C., D’Souza, J. and Batterman, S. (2008) “Distributions of personal VOC exposures: A population-based analysis.” Environment international, 34(7), 922–931.
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Kim, Y. M., Harrad, S. and Harrison, R. M. (2001) “Concentrations and sources of VOCs in urban domestic and public microenvironments.” Environmental Science and Technology, 35(6), 997–1004.
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Kwon, K. D, Jo, W. K., Lim, H. J. and Jeong, W. S. (2008) “Volatile pollutants emitted from selected liquid household products.” Environmental Science and Pollution Research, 15(6), 521–526.
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Kwon, K. D., Jo, W. K., Lim, H. J. and Jeong, W. S. (2007) “Characterization of emissions composition for selected household products available in Korea.” Journal of hazardous materials, 148(1–2), 192–198.
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Meek, M. E. and Klaunig, J. E. (2010) “Proposed mode of action of benzene-induced leukemia: Interpreting available data and identifying critical data gaps for risk assessment.” Chemico-biological interactions, 184(1–2), 279–285.
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Missia, D. A., Demetriou, E., Michael, N., Tolis, E. I. and Bartzis, J. G. (2010) “Indoor exposure from building materials: A field study.” Atmospheric Environment, 44(35), 4388–4395.
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OEHHA. (2001) “Public Health Goal for Benzene in Drinking Water.” Office of Environmental Health Hazard Assessment, California Environmental Protection Agency, Sacramento, CA. Available at www.oehha.ca.gov/water/phg/pdf/ BenzeneFinPHG.pdf.
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Park, J. S. and Ikeda, K. (2006) “Variations of formaldehyde and VOC levels during 3 years in new and older homes.” Indoor air, 16(2), 129–135.
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Rinsky, R. A., Young, R. J. and Smith, A. B. (1981) “Leukemia in benzene workers.” American Journal of Industrial Medicine, 2(3), 217–245.
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Sack, T. M., Steele, D. H., Hammerstrom, K. and Remmers, J. (1992) “A survey of household products for volatile organic compounds.” Atmospheric Environment — Part A General Topics, 26 A(6), 1063–1070.
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U.S. EPA. (2000) United States Environmental Protection Agency. Integrated Risk Information System. Benzene (CASRN 71-43-2). Last updated on 2010-03-16 (www.epa. gov/iris/subst/0276.htm#refinhal).
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U.S. EPA. (1998) “Carcinogenic effects of benzene: An update.” National Centre for Environmental Assessment, Office of Research and Development, U.S. Environmental Protection Agency, Washington, DC (EPA/600/P-97/001F) [as cited in Health Canada 2009].
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U.S. EPA. (1992) “Indoor Air Quality Data Base for Organic Compounds.” United States Environmental Protection Agency. EPA-600-R-92-025. Washington, D.C.
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Wallace, L. A., Pellizzari, E. and Leaderer, B. (1987) “Emission of volatile organic compounds from building materials and consumer products.” Atmospheric Environment, 21(2), 385–393.
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WHO. (2010) WHO guidelines for indoor air quality: selected pollutants. World Health Organization Regional Office for Europe. Available at www.euro.who.int/__data/assets/pdf_file/ 0009/128169/e94535.pdf.
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Won, D., Magee, R. J., Yang, W., Lusztyk, E., Nong, G. and Shaw, C. Y. (2005) “A material emission database for 90 target VOCs.” Indoor Air 2005, The 10th International Conference on Indoor Air Quality and Climate, Beijing, China, Sept. 4–9, 2005, 1–6. Available at www.archive.nrc-cnrc.gc.ca/obj/irc/ doc/pubs/nrcc48314/nrcc48314.pdf.
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Yu, C. and Crump, D. (1998) “A review of the emission of VOCs from polymeric materials used in buildings.” Building and Environment, 33(6), 357–374.
[37-1-o]
DEPARTMENT OF HEALTH
HAZARDOUS MATERIALS INFORMATION REVIEW ACT
Filing of claims for exemption
Pursuant to paragraph 12(1)(a) of the Hazardous Materials Information Review Act, the Chief Screening Officer of the Workplace Hazardous Materials Directorate hereby gives notice of the filing of the claims for exemption listed below.
In accordance with subsection 12(2) of the Hazardous Materials Information Review Act, affected parties may make written representations to the screening officer with respect to the claim for exemption and the material safety data sheet to which it relates. “Affected parties” means a person who is not a competitor of the claimant and who uses, supplies or is otherwise involved in the use or supply of the controlled product at a work place, and includes
- (a) a supplier of the controlled product;
- (b) an employee at the work place;
- (c) an employer at the work place;
- (d) a safety and health professional for the work place;
- (e) a safety and health representative or a member of a safety and health committee for the work place; and
- (f) a person who is authorized in writing to represent
- (i) a supplier referred to in paragraph (a) or an employer referred to in paragraph (c), or
- (ii) an employee referred to in paragraph (b), except where that person is an official or a representative of a trade union that is not certified or recognized in respect of the work place.
Written representations respecting a claim for exemption cited in the present notice, or respecting the material safety data sheet or label to which the claim relates, must cite the appropriate registry number, state the reasons and evidence upon which the representations are based and be delivered within 30 days of the date of the publication of this notice in the Canada Gazette, Part Ⅰ, to the screening officer at the following address: Workplace Hazardous Materials Directorate, 427 Laurier Avenue W, 7th Floor, Ottawa, Ontario K1A 0K9.
STEPHANIE REID
Chief Screening Officer
The claim listed below seeks a business exemption from the disclosure of employer confidential information in respect of a controlled product. The confidential information would otherwise be required to be disclosed by the provisions of the applicable provincial legislation relating to occupational health and safety.
| Claimant | Subject of the Claim for Exemption | Product Identifier (As shown on the MSDS) | Registry Number |
|---|---|---|---|
| Greensolv Inc., Baie-D’Urfé, Quebec | Chemical identity and concentration of three ingredients | G-Strip 255-8ADD | 9002 |
The claims listed below seek exemption from the disclosure of supplier confidential business information in respect of a controlled product; such disclosure would otherwise be required under the provisions of the Hazardous Products Act.
| Claimant | Subject of the Claim for Exemption | Product Identifier (As shown on the MSDS) | Registry Number |
|---|---|---|---|
| Baker Petrolite Corp., Sugar Land, Texas | Chemical identity of one ingredient | PETROSWEET(TM) HS03507 H2S SCAVENGER | 8849 |
| Baker Petrolite Corp., Sugar Land, Texas | Chemical identity of five ingredients | CRONOX(TM) 277 Corrosion Inhibitor | 8850 |
| Stepan Company, Northfield, Illinois | Chemical identity of one ingredient | PETROSTEP S-3B | 8851 |
| Stepan Company, Northfield, Illinois | Chemical identity of two ingredients | PETROSTEP S-13D HA | 8852 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of two ingredients | UCARSOL(TM) NH SOLVENT 602 | 8853 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of two ingredients | UCARSOL(TM) AP SOLVENT 810 | 8854 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of two ingredients | UCARSOL(TM) NH SOLVENT 608 | 8855 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of two ingredients | UCARSOL(TM) AP SOLVENT 814 | 8856 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of two ingredients | UCARSOL(TM) AP SOLVENT 804 | 8857 |
| Air Products & Chemicals, Inc., Allentown, Pennsylvania | Chemical identity of one ingredient | Ancamide® 702 B75 Curing Agent | 8858 |
| DuPont Electronic Technologies-MCM, Raleigh, North Carolina | Chemical identity of one ingredient | 5880 | 8859 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of two ingredients | EMBREAK 2W2014 | 8860 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of one ingredient | PETROFLO 20Y3416 | 8861 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of one ingredient | PROSWEET S1761 | 8862 |
| Momentive Performance Materials, Markham, Ontario | Chemical identity of four ingredients | M90033 12C Sealant | 8863 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of one ingredient | SPEC-AID 8Q403ULS | 8864 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of two ingredients | THERMOFLO 7031 | 8865 |
| Baker Petrolite Corp., Sugar Land, Texas | Chemical identity of three ingredients | TOLAD™ 3514 ADDITIVE | 8866 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity of one ingredient | NALCO® DVP6P011 | 8867 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity of one ingredient | NALCO® DVP6P012 | 8868 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity of four ingredients | NALCO® VX10987 | 8869 |
| 3M Canada Company, London, Ontario | Chemical identity of four ingredients | 3M™ HEAVY DUTY MULTI-SURFACE CLEANER Concentrate (Twist ’n Fill™ Product No. 2) | 8870 |
| E.I. DuPont Canada Company, Mississauga, Ontario | Chemical identity of one ingredient | DuPont™ Capstone® FS-31 | 8871 |
| E.I. DuPont Canada Company, Mississauga, Ontario | Chemical identity of one ingredient | DuPont™ Capstone® CP | 8872 |
| 3M Canada Company, London, Ontario | Chemical identity of one ingredient | SCOTCHKOTE 207R Rough Overcoating | 8873 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity of six ingredients | NALCO® VX10902 | 8874 |
| Engenium Chemicals Corporation, Calgary, Alberta | Chemical identity and concentration of two ingredients | ZX-102 | 8875 |
| Hydro Technologies (Canada) Inc., Québec, Quebec | Chemical identity and concentration of one ingredient | HY BRITE(R) DB | 8876 |
| 3M Canada Company, London, Ontario | Chemical identity of two ingredients | SCOTCH-WELD(TM) STRUCTURAL ADHESIVE FILM, AF 163-2 | 8877 |
| Engenium Chemicals Corporation, Calgary, Alberta | Chemical identity and concentration of two ingredients | OPTIPLUS | 8878 |
| Calfrac Well Services Ltd., Calgary, Alberta | Chemical identity and concentration of three ingredients | DWP-124 | 8879 |
| Baker Petrolite Corp., Sugar Land, Texas | Chemical identity of one ingredient | TOLAD™ 3060 ADDITIVE | 8880 |
| 3M Canada Company, London, Ontario | Chemical identity of two ingredients | Scotchkote 413 Spray Grade Fusion Bonded Epoxy Coating | 8881 |
| Afton Chemical Corporation, Richmond, Virginia | Chemical identity of three ingredients | HiTEC® 388 Performance Additive | 8882 |
| Afton Chemical Corporation, Richmond, Virginia | Chemical identity of six ingredients | HiTEC® 348 Performance Additive | 8883 |
| Afton Chemical Corporation, Richmond, Virginia | Chemical identity of three ingredients | HiTEC® 397G Performance Additive | 8884 |
| 3M Canada Company, London, Ontario | Chemical identity of two ingredients | 3M™ Anisotropic Conductive Film 7376-30 | 8885 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity of one ingredient | pHREEdom® 5200M | 8886 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity of one ingredient | NALCO® OS2190 | 8887 |
| Rohm and Haas Canada LP, West Hill, Ontario | Chemical identity of one ingredient | PARALOID ™ EXL-2650A Engineering Resin Additive | 8888 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity of two ingredients | UCARSOL™ HS SOLVENT 133 | 8889 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of two ingredients | UCARSOL™ HS SOLVENT 102 | 8890 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity of two ingredients | TRITON™ DF-20 Surfactant | 8891 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of two ingredients | Losalt LS1512 | 8892 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of three ingredients | Inhibitor VCS2000 | 8893 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of one ingredient | Losalt LS1521 | 8894 |
| GE Water & Process Technologies Canada, Oakville, Ontario | Chemical identity and concentration of three ingredients | Petroflo 20Y3450 | 8895 |
| Chevron Oronite Company LLC, Bellaire, Texas | Chemical identity of one ingredient | LUBAD® 1817 | 8896 |
| Stepan Company, Northfield, Illinois | Chemical identity of three ingredients | TOXIMUL 8362 | 8898 |
| Momentive Performance Materials, Markham, Ontario | Chemical identity of one ingredient | Niax® silicone L-878 | 8899 |
| Chevron Oronite Company LLC, Bellaire, Texas | Chemical identity of one ingredient | OLOA® 55508 | 8900 |
| 3M Canada Company, London, Ontario | Chemical identity of one ingredient | Scotchkote 626-155 Fusion Bonded Epoxy Coating | 8901 |
| ZEC Lubrication Inc., Ottawa, Ontario | Chemical identity and concentration of one ingredient | AC-XL | 8902 |
| Arkema Canada Inc., Burlington, Ontario | Chemical identity of two ingredients | LUPEROX® RTM | 8903 |
| Rohm and Haas Canada LP, West Hill, Ontario | Chemical identity of three ingredients | PARALOID™EXL-2314 IMPACT MODIFIER | 8904 |
| PMC ORGANOMETALLIX, Mount Laurel, New Jersey | Chemical identity and concentration of one ingredient | THERMOLITE 176 | 8905 |
| PMC ORGANOMETALLIX, Mount Laurel, New Jersey | Chemical identity and concentration of two ingredients | THERMOLITE 178 | 8906 |
| PMC ORGANOMETALLIX, Mount Laurel, New Jersey | Chemical identity and concentration of two ingredients | THERMOLITE 140 | 8907 |
| Innospec Fuel Specialties, Newark, Delaware | Chemical identity of one ingredient | DDA-3525 IA2 | 8908 |
| BASF Canada Inc., Mississauga, Ontario | Chemical identity of one ingredient | Plurafac SLF 180 | 8909 |
| Cytec Industries Inc., Woodland Park, New Jersey | Chemical identity of one ingredient | CYASORB(R) 390C Stabilizer | 8910 |
| Multi-Chem Production Chemicals Co., Calgary, Alberta | Chemical identity of two ingredients | RockOn ™ MX 5-3120 | 8911 |
| Multi-Chem Production Chemicals Co., Calgary, Alberta | Chemical identity and concentration of one ingredient | MC SS-5041 | 8912 |
| Multi-Chem Production Chemicals Co., Calgary, Alberta | Chemical identity and concentration of one ingredient | MC MX 2-2822 | 8913 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of one ingredient | DETACK EC9444D | 8914 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of three ingredients | NALCO® VX11001 | 8915 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of one ingredient | DETACK EC9440D | 8916 |
| MeadWestvaco Corp. Specialty Chemicals Div., North Charleston, South Carolina | Chemical identity and concentration of two ingredients | MORLIFE(TM) 5000 | 8917 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of one ingredient | DETACK EC9451D | 8918 |
| Allnex Canada Inc., c/o Goodmans, LLP, Toronto, Ontario | Chemical identity and concentration of two ingredients | EBECRYL(R) 81 radiation curing resins | 8919 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of three ingredients | DOW(TM) IC 210 Gas Conditioning Chelate | 8920 |
| Dow Chemical Canada ULC, Calgary, Alberta | Chemical identity and concentration of one ingredient | DOW(TM) CA-2003 Sulfur Conditioning Additive | 8921 |
| E.I. DuPont Canada Company, Mississauga, Ontario | Chemical identity and concentration of one ingredient | Capstone(R) LPA | 8922 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | AS-9 Anti-Sludging Agent | 8923 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | AS-7 Anti-Sludging Agent | 8924 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | A-Sperse | 8925 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | 19N | 8926 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | CL-11 CROSSLINKER | 8927 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | CL-41 | 8928 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | CleanLink | 8929 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | FDP-S1047-12 | 8930 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | BC-200 UC | 8931 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | CAT-3 ACTIVATOR | 8932 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | Cla-Web (TM) | 8933 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | Clayfix II Plus | 8934 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | CLAYFIX II MATERIAL | 8935 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | CT-ARMOR | 8936 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | ES-5 PROPLOK SURFACTANT | 8937 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | FDP-S821-06 | 8938 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | G-SPERSE | 8939 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | HAI-404 (TM) | 8940 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | GasPerm 1000™ | 8941 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | GasPerm 1100 | 8942 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | HAI-OS ACID INHIBITOR | 8943 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | HC-2 | 8944 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | HII-500M CORROSION INHIBITOR INTENSIFIER | 8945 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | HZ-20 | 8946 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | LCA-1 | 8947 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | MO-86M | 8948 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | MUSOL A SOLVENT | 8949 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | PARASPERSE CLEANER | 8950 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | PEN-88M | 8951 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | SGA-HT M Gelling Agent | 8952 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | SPERSE-ALL M | 8953 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | SSO-21M WINTERIZED | 8954 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | WS-36 EMULSIFYING AGENT | 8955 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | WS-36M | 8956 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | MO-85M | 8957 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of six ingredients | NALCO® EC1630A | 8958 |
| Hydro Technologies (Canada) Inc., Québec, Quebec | Chemical identity and concentration of two ingredients | HY BRITE(R) DB-1300 | 8959 |
| Trican Well Service Ltd., Calgary, Alberta | Chemical identity and concentration of one ingredient | TXP-17 | 8960 |
| Les Spécialités L.E.N., Granby, Quebec | Chemical identity and concentration of one ingredient | Cleanearth™ Scalecide | 8961 |
| Les Spécialités L.E.N., Granby, Quebec | Chemical identity and concentration of one ingredient | Cleanearth™ Envirocide | 8962 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of five ingredients | CLEAN N COR (R) EC1579W | 8963 |
| Trican Well Service Ltd., Calgary, Alberta | Chemical identity and concentration of one ingredient | TXP-18 | 8964 |
| Babcock-Hitachi K.K., Kure-Shi, Hiroshima-Ken | Chemical identity and concentration of one ingredient | H3-1 | 8965 |
| W-TECH Technologies Ltd., Vancouver, British Columbia | Chemical identity and concentration of three ingredients | MD800 | 8966 |
| Chevron Oronite Company LLC, Bellaire, Texas | Chemical identity and concentration of two ingredients | OLOA® 40814 | 8967 |
| Chevron Oronite Company LLC, Bellaire, Texas | Chemical identity and concentration of two ingredients | MAR501S | 8968 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of six ingredients | NALCO® VX10986 | 8969 |
| Calfrac Well Services Ltd., Calgary, Alberta | Chemical identity and concentration of one ingredient | DAP-634 | 8970 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of one ingredient | BREAXIT® SP177 | 8971 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of one ingredient | BREAXIT® SP354 | 8972 |
| SSC Inc., Hamilton, Ontario | Chemical identity and concentration of three ingredients | SCL 802IC | 8973 |
| 3M Canada Company, London, Ontario | Chemical identity and concentration of two ingredients | 3M(TM) 8805UV Black Piezo Inkjet Ink | 8974 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of three ingredients | NALCO® EC9453A | 8975 |
| MeadWestvaco Corp. Specialty Chemicals Div., North Charleston, South Carolina | Chemical identity and concentration of one ingredient | INDULIN® 814A | 8976 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | LGC-VI UC | 8977 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | FDP-S867A-07 | 8978 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | CAS-1 | 8979 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of one ingredient | MO-85 LP | 8980 |
| Halliburton Energy Services, Inc., Houston, Texas | Chemical identity and concentration of two ingredients | D-AIR 3000W | 8981 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of six ingredients | NALCO® EC1632A | 8982 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of two ingredients | ASP® FNE200 | 8983 |
| Evonik Corporation, Parsippany, New Jersey | Chemical identity and concentration of one ingredient | Dynasylan® HYDROSIL 1151 | 8984 |
| Trican Well Service Ltd., Calgary, Alberta | Chemical identity and concentration of two ingredients | SS-5 | 8985 |
| Nalco Canada Co., Burlington, Ontario | Chemical identity and concentration of four ingredients | NALCO® EC1417A | 8986 |
| Italmatch Chemicals S.p.A., San Benigno, Genova | Chemical identity and concentration of two ingredients | SPE 0108 | 8987 |
| Italmatch Chemicals S.p.A., San Benigno, Genova | Chemical identity and concentration of two ingredients | SPE 0001 | 8988 |
| Lubrizol Corporation, Wickliffe, Ohio | Chemical identity and concentration of two ingredients | LUBRIZOL® CV9601 | 8989 |
| Dow Corning Corporation, Midland, Michigan | Chemical identity and concentration of one ingredient | DOW CORNING(R) XX-1060 THERMALLY CONDUCTIVE MATERIAL | 8990 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of two ingredients | EBECRYL® 8414 radiation curing resins | 8991 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 3708 radiation curing resins | 8992 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of two ingredients | EBECRYL® 860 radiation curing resins | 8993 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of two ingredients | EBECRYL® 450 radiation curing resins | 8994 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 83 radiation curing resins | 8995 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 168 radiation curing resins | 8996 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 350 radiation curing resins | 8997 |
| Lubrizol Corporation, Wickliffe, Ohio | Chemical identity and concentration of one ingredient | AMIDEX(TM) 1248 SURFACTANT | 8998 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 438 radiation curing resins | 8999 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 220 radiation curing resins | 9000 |
| Allnex Canada Inc., (c/o Goodmans, LLP), Toronto, Ontario | Chemical identity and concentration of one ingredient | EBECRYL® 265 radiation curing resins | 9001 |
| Kop-Coat, St. Louis, Missouri | Chemical identity and concentration of three ingredients | DRI-WRAP (5-13) | 9003 |
[37-1-o]
DEPARTMENT OF INDUSTRY
CANADA CORPORATIONS ACT
Application for surrender of charter
| File No. | Name of Company | Received |
|---|---|---|
| 176695-3 | KAMADHENU MEDICAL RELIEF INCORPORATED | 14/08/2013 |
September 6, 2013
MARCIE GIROUARD
Director
For the Minister of Industry
[37-1-o]
DEPARTMENT OF INDUSTRY
CANADA CORPORATIONS ACT
Supplementary letters patent
| File No. | Name of Company | Date of S.L.P. |
|---|---|---|
| 759409-7 | Islamic Society of Regina | 07/08/2013 |
| 292425-1 | THE MCCORD MUSEUM FOUNDATION/ LA FONDATION DU MUSÉE MCCORD | 05/07/2013 |
| 283294-1 | THE ORGANIZATION OF MILITARY MUSEUMS OF CANADA, INC./ L’ORGANISATION DES MUSEES MILITAIRES DU CANADA, INC. | 26/07/2013 |
September 6, 2013
MARCIE GIROUARD
Director
For the Minister of Industry
[37-1-o]
DEPARTMENT OF INDUSTRY
CANADA CORPORATIONS ACT
Supplementary letters patent — Name change
| File No. | Old Name of Company | New Name of Company | Date of S.L.P. |
|---|---|---|---|
| 432359-9 | CCPI CANADIAN CENTRE FOR POLICY INGENUITY/ CCPI CENTRE CANADIEN DES POLITIQUES INGÉNIEUSES | Good Done Well | 01/08/2013 |
| 444136-2 | CLINTON GIUSTRA SUSTAINABLE GROWTH INITIATIVE (CANADA) | Clinton Giustra Enterprise Partnership (Canada) | 17/07/2013 |
| 406618-9 | THE ALGONQUIN TO ADIRONDACKS CONSERVATION ASSOCIATION (AACA) L’ASSOCIATION DE CONSERVATION ALGONQUIN ADIRONDACKS (AACA) | Algonquin to Adirondacks Collaborative (A2A) La Collective d’Algonquin à Adirondacks (A2A) | 11/04/2013 |
| 367922-5 | THE HISTORICA-DOMINION INSTITUTE / INSTITUT HISTORICA-DOMINION | Historica Canada | 03/09/2013 |
September 6, 2013
MARCIE GIROUARD
Director
For the Minister of Industry
[37-1-o]
DEPARTMENT OF INDUSTRY
RADIOCOMMUNICATION ACT
Notice No. SMSE-007-13 — Consultation on use of the frequency band 25.05-25.25 GHz
This notice announces Industry Canada’s launch of the above-mentioned public consultation to clarify the use of the band 25.05-25.25 GHz, which is shared between fixed service systems and fixed-satellite service systems.
The proposals presented in the consultation paper are intended to facilitate the shared use of the band by systems in the fixed service and the fixed-satellite service. This goal satisfies the objective of the Spectrum Policy Framework for Canada to maximize the potential economic and social benefits that Canadians derive from the use of the radio frequency spectrum.
Submitting comments
Interested parties are invited to submit comments on the consultation paper. These comments are to be submitted within 60 days of the publication of this notice in the Canada Gazette. Soon after the close of the comment period, all comments received will be posted on Industry Canada’s Spectrum Management and Telecommunications Web site at www.ic.gc.ca/ spectrum.
Respondents are requested to provide their comments to the following email address: spectrum.planning@ic.gc.ca. Other electronic formats, such as Microsoft Word or Adobe PDF, will also be accepted.
Written submissions should be addressed to the Director General, Engineering, Planning and Standards Branch, Industry Canada (JETN), 235 Queen Street, Ottawa, Ontario K1A 0H5.
All submissions should cite the Canada Gazette, Part Ⅰ, the publication date, the title and the notice reference number (SMSE-007-13).
Obtaining copies
Copies of this notice and of documents referred to herein are available electronically on Industry Canada’s Spectrum Management and Telecommunications Web site at www.ic.gc.ca/spectrum.
Official versions of Canada Gazette notices can be viewed at www.gazette.gc.ca/rp-pr/p1/index-eng.html. Printed copies of the Canada Gazette can be ordered by telephoning the sales counter of Publishing and Depository Services at 613-941-5995 or 1-800-635-7943.
August 28, 2013
MARC DUPUIS
Director General
Engineering, Planning and Standards Branch
[37-1-o]
DEPARTMENT OF INDUSTRY
RADIOCOMMUNICATION ACT
Notice No. SMSE-019-13 — Release of SRSP-325.25, Issue 1: Technical Requirements for Fixed Radio Systems Operating in the Bands 25.25-26.5 GHz and 27.5-28.35 GHz
Notice is hereby given that Industry Canada is releasing Standard Radio System Plan SRSP-325.25, Issue 1: Technical Requirements for Fixed Radio Systems Operating in the Bands 25.25-26.5 GHz and 27.5-28.35 GHz, which sets out the minimum technical requirements for the efficient use of these bands.
General information
SRSP-325.25, Issue 1, will come into force as of the date of publication of this notice.
Any inquiries regarding SRSP-325.25 should be directed to the Manager, Fixed Wireless Systems, 613-991-0035 (telephone), 613-952-5108 (fax), srsp.pnrh@ic.gc.ca (email).
Interested parties should submit their comments within 120 days of the date of publication of this notice. Soon after the close of the comment period, all comments received will be posted on Industry Canada’s Spectrum Management and Telecommunications Web site at www.ic.gc.ca/spectrum.
Submitting comments
Respondents are requested to provide their comments in electronic format (Microsoft Word or Adobe PDF) to the Manager, Fixed Wireless Systems.
Written submissions should be addressed to the Director General, Engineering, Planning and Standards Branch, Industry Canada, 235 Queen Street (JETN19), Ottawa, Ontario K1A 0H5. All submissions should cite the Canada Gazette, Part Ⅰ, the publication date, the title and the notice reference number (SMSE-019-13).
Obtaining copies
Copies of this notice and of documents referred to herein are available electronically on Industry Canada’s Spectrum Management and Telecommunications Web site at www.ic.gc.ca/spectrum.
Official versions of Canada Gazette notices can be viewed at www.gazette.gc.ca/rp-pr/p1/index-eng.html. Printed copies of the Canada Gazette can be ordered by telephoning the sales counter of Publishing and Depository Services at 613-941-5995 or 1-800-635-7943.
August 8, 2013
MARC DUPUIS
Director General
Engineering, Planning and Standards Branch
[37-1-o]
OFFICE OF THE SUPERINTENDENT OF FINANCIAL INSTITUTIONS
BANK ACT
Rogers Bank — Order to commence and carry on business
Notice is hereby given of the issuance, pursuant to subsection 49(1) of the Bank Act, of an order to commence and carry on business authorizing Rogers Bank to commence and carry on business, effective August 23, 2013.
August 30, 2013
JULIE DICKSON
Superintendent of Financial Institutions
[37-1-o]